Development and evaluation of a harmonized physiologically based pharmacokinetic (PBPK) model for perchloroethylene toxicokinetics in mice, rats, and humans

This article reports on the development of a “harmonized” PBPK model for the toxicokinetics of perchloroethylene (tetrachloroethylene or perc) in mice, rats, and humans that includes both oxidation and glutathione (GSH) conjugation of perc, the internal kinetics of the oxidative metabolite trichloroacetic acid (TCA), and the urinary excretion kinetics of the GSH conjugation metabolites N-Acetylated trichlorovinyl cysteine and dichloroacetic acid. The model utilizes a wider range of in vitro and in vivo data than any previous analysis alone, with in vitro data used for initial, or “baseline,” parameter estimates, and in vivo datasets separated into those used for “calibration” and those used for “evaluation.” Parameter calibration utilizes a limited Bayesian analysis involving flat priors and making inferences only using posterior modes obtained via Markov chain Monte Carlo (MCMC). As expected, the major route of elimination of absorbed perc is predicted to be exhalation as parent compound, with metabolism accounting for less than 20% of intake except in the case of mice exposed orally, in which metabolism is predicted to be slightly over 50% at lower exposures. In all three species, the concentration of perc in blood, the extent of perc oxidation, and the amount of TCA production is well-estimated, with residual uncertainties of ~ 2-fold. However, the resulting range of estimates for the amount of GSH conjugation is quite wide in humans (~ 3000-fold) and mice (~ 60-fold). While even high-end estimates of GSH conjugation in mice are lower than estimates of oxidation, in humans the estimated rates range from much lower to much higher than rates for perc oxidation. It is unclear to what extent this range reflects uncertainty, variability, or a combination. Importantly, by separating total perc metabolism into separate oxidative and conjugative pathways, an approach also recommended in a recent National Research Council review, this analysis reconciles the disparity between those previously published PBPK models that concluded low perc metabolism in humans and those that predicted high perc metabolism in humans. In essence, both conclusions are consistent with the data if augmented with some additional qualifications: in humans, oxidative metabolism is low, while GSH conjugation metabolism may be high or low, with uncertainty and/or interindividual variability spanning three orders of magnitude. More direct data on the internal kinetics of perc GSH conjugation, such as trichlorovinyl glutathione or tricholorvinyl cysteine in blood and/or tissues, would be needed to better characterize the uncertainty and variability in GSH conjugation in humans.     

Liver tumor induction in B6C3F1 mice by dichloroacetate and trichloroacetate

Male and female B6C3F1 mice were administered dichloroacetate (DCA) and trichloroacetate (TCA) in their drinking water at concentrations of 1 or 2 g/l for up to 52 weeks. Both compounds induced hepatoproliferative lesions (HPL) in male mice, including hepatocellular nodules, adenomas and hepatocellular carcinomas within 12 months. The induction of HPL by TCA was linear with dose. In contrast, the response to DCA increased sharply with the increase in concentration from 1 to 2 g/l. Suspension of DCA treatment at 37 weeks resulted in the same number of HPL at 52 weeks that would have been predicted on the basis of the total dose administered. However, none of the lesions in this treatment group progressed to hepatocellular carcinomas. Conversely, the yield of HPL at 52 weeks when TCA treatment was suspended at 37 weeks was significantly below that which would have been predicted by the total dose administered. In this case, 3 of 5 remaining lesions were hepatocellular carcinomas. Throughout active treatment DCA-treated mice displayed greatly enlarged livers characterized by a marked cytomegaly and massive accumulations of glycogen in hepatocytes throughout the liver. Areas of focal necrosis were seen throughout the liver. TCA produced small increases in cell size and much a more modest accumulation of glycogen. Focal necrotic damage did not occur in TCA-treated animals. TCA produced marked accumulations of lipofuscin in the liver. Lipofuscin accumulation was less marked with DCA. These data confirm earlier observations that DCA and TCA are capable of inducing hepatic tumors in B6C3F1 mice and argue that the mechanisms involved in tumor induction differ substantially between these two similar compounds. Tumorigenesis by DCA may depend largely on stimulation of cell division secondary to hepatotoxic damage. On the other hand, TCA appears to increase lipid peroxidation, suggesting that production of radicals may be responsible for its effects.     

Inhalation carcinogenicity of 1,1,1-trichloroethane in rats and mice

Abstract

Carcinogenicity of 1,1,1-trichloroethane (TCE) was examined by an inhalation exposure of F344 rats and BDF1 mice of both sexes to TCE at 0, 200, 800 or 3200?ppm for 6?h/d, 5?d/week for 104 weeks. In male rats, the incidences of bronchiolo-alveolar adenomas and peritoneal mesotheliomas were significantly increased in the 800 and 3200?ppm-exposed groups, respectively. The incidence of bronchiolo-alveolar adenomas in the 3200?ppm-exposed groups exceeded the range of historical control data in the Japan Bioassay Research Center. In female rats, the tumor incidences were not increased in any organs of the TCE-exposed groups. In male mice, a significant positive trend with dose was shown for incidences of bronchiolo-alveolar carcinomas, combined incidences of bronchiolo-alveolar adenomas/carcinomas and hepatocellular adenomas. The incidence of Harderian gland adenomas was significantly increased in the 3200?ppm-exposed group, and malignant lymphomas of spleen at this highest dose exceeded the range of historical control data. In female mice, the combined incidence of bronchiolo-alveolar adenomas/carcinomas was significantly increased in the 3200?ppm-exposed group, and the incidences of hepatocellular adenomas and combined incidences of hepatocellular adenomas/carcinomas were significantly increased in the 200, 800 and 3200?ppm-exposed groups with dose dependence except the combined incidence of hepatocellular adenomas/carcinomas in the 200?ppm-exposed group. The incidences of bronchiolo-alveolar adenomas in the 3200?ppm-exposed group and combined incidences of hepatocellular adenomas/carcinomas in the 200?ppm-exposed groups exceeded the ranges of historical control data. Thus, this study provided clear evidence of inhalation carcinogenicity for TCE in both rats and mice.     

Development of an updated PBPK model for trichloroethylene and metabolites in mice, and its application to discern the role of oxidative metabolism in TCE-induced hepatomegaly

Trichloroethylene (TCE) is a lipophilic solvent rapidly absorbed and metabolized via oxidation and conjugation to a variety of metabolites that cause toxicity to several internal targets. Increases in liver weight (hepatomegaly) have been reported to occur quickly in rodents after TCE exposure, with liver tumor induction reported in mice after long-term exposure. An integrated dataset for gavage and inhalation TCE exposure and oral data for exposure to two of its oxidative metabolites (TCA and DCA) was used, in combination with an updated and more accurate physiologically-based pharmacokinetic (PBPK) model, to examine the question as to whether the presence of TCA in the liver is responsible for TCE-induced hepatomegaly in mice. The updated PBPK model was used to help discern the quantitative contribution of metabolites to this effect. The update of the model was based on a detailed evaluation of predictions from previously published models and additional preliminary analyses based on gas uptake inhalation data in mice. The parameters of the updated model were calibrated using Bayesian methods with an expanded pharmacokinetic database consisting of oral, inhalation, and iv studies of TCE administration as well as studies of TCE metabolites in mice. The dose-response relationships for hepatomegaly derived from the multi-study database showed that the proportionality of dose to response for TCE- and DCA-induced hepatomegaly is not observed for administered doses of TCA in the studied range. The updated PBPK model was used to make a quantitative comparison of internal dose of metabolized and administered TCA. While the internal dose of TCA predicted by modeling of TCE exposure (i.e., mg TCA/kg-d) showed a linear relationship with hepatomegaly, the slope of the relationship was much greater than that for directly administered TCA. Thus, the degree of hepatomegaly induced per unit of TCA produced through TCE oxidation is greater than that expected per unit of TCA administered directly, which is inconsistent with the hypothesis that TCA alone accounts for TCE-induced hepatomegaly. In addition, TCE-induced hepatomegaly showed a much more consistent relationship with PBPK model predictions of total oxidative metabolism than with predictions of TCE area-under-the-curve in blood, consistent with toxicity being induced by oxidative metabolites rather than the parent compound. Therefore, these results strongly suggest that oxidative metabolites in addition to TCA are necessary contributors to TCE-induced liver weight changes in mice.     

The carcinogenicity of trichloroethylene and its metabolites, trichloroacetic acid and dichloroacetic acid, in mouse liver

Trichloroethylene (TCE) has previously been shown to be carcinogenic in mouse liver when administered by daily gavage in corn oil. The metabolism of TCE results, in part, in the formation of trichloroacetic acid (TCA) as a major metabolite and dichloroacetic acid (DCA) as a minor metabolite. These chlorinated acetic acids have not been shown to be genotoxic, although they have been shown to induce peroxisome proliferation. Therefore, we determined the ability they have been shown to induce peroxisome proliferation. Therefore, we determined the ability of TCE, TCA, or DCA to act as tumor promoters in mouse liver. Male B6C3F1 mice were administered intraperitoneally 0, 2.5, or 10 micrograms/g body wt ethylnitrosourea (ENU) on Day 15 of age. At 28 days of age, the mice were placed on drinking water containing either TCE (3 or 40 mg/liter), TCA (2 or 5 g/liter), or DCA (2 or 5 g/liter). All drinking waters were neutralized with NaOH to a final pH of 6.5-7.5. The animals were killed after 61 weeks of exposure to the treated drinking water (65 weeks of age). Both DCA and TCA at a concentration of 5 g/liter were carcinogenic without prior initiation with ENU, resulting in hepatocellular carcinomas in 81 and 32% of the animals, respectively. DCA and TCA also increased the incidence of animals with adenomas and the number of adenomas/animal in those animals that were not initiated with ENU. While 2.5 micrograms/g body wt ENU followed by NaCl in the drinking water resulted in only 5% of the animals with hepatocellular carcinomas, 2.5 micrograms/g body wt ENU followed with 2 or 5 g/liter DCA resulted in a 66 or 78% incidence of carcinoma, respectively, or, followed with 2 or 5 g/liter TCA, resulted in a 48% incidence at either concentration. None of the untreated animals had hepatocellular carcinomas. Therefore our results demonstrate that DCA and TCA are complete hepatocarcinogens in B6C3F1 mice.     

Carcinogenicity and chronic toxicity of hydrazine monohydrate in rats and mice by two-year drinking water treatment

The carcinogenicity and chronic toxicity of hydrazine monohydrate was examined by administrating hydrazine monohydrate in drinking water to groups of 50 F344/DuCrj rats and 50 Crj:BDF₁ mice of both sexes for two years. The drinking water concentration of hydrazine monohydrate was 0, 20, 40 or 80 ppm (wt/wt) for male and female rats and male mice; and 0, 40, 80 or 160 ppm for female mice. Survival rates of each group of males and females rats and mice were similar to the respective controls, except female rats administered 80 ppm. Two-year administration of hydrazine monohydrate produced an increase in the incidences of hepatocellular adenomas and carcinomas in rats of both sexes along with hepatic foci. In mice, the incidences of hepatocellular adenomas and carcinomas were increased in females, and significantly increased incidences of hepatocellular adenomas in females administered 160 ppm were observed. Thus, hydrazine monohydrate is carcinogenic in two species, rats and mice. Additionally, non-neoplastic renal lesions in rats and mice and non-neoplastic nasal lesions in mice were observed.     

Carcinogenicity of <Emphasis Type="Italic">ortho</Emphasis>-phenylenediamine dihydrochloride in rats and mice by two-year drinking water treatment

The carcinogenicity of ortho-phenylenediamine (o-PD) was examined by administrating o-phenylenediamine dihydrochloride (o-PD2HCl) in dinking water to groups of 50 F344/DuCrj rats and 50 Crj:BDF₁ mice of both sexes for 2 years. The drinking water concentration of o-PD2HCl was 0, 500, 1,000 or 2,000 ppm (wt/wt) for male rats; 0, 250, 500 or 1,000 ppm for female rats; 0, 500, 1,000 or 2,000 ppm for male mice; and 0, 1,000, 2,000 or 4,000 ppm for female mice. Two-year administration of o-PD2HCl produced a dose-dependent increase in the incidences of hepatocellular adenomas and carcinomas in rats of both sexes and in female mice, and hepatocellular adenomas in male mice. In mice, the incidences of hepatocellular adenomas were increased at the lowest dose used in both males and females. Metastasis from hepatocellular carcinomas of rats occurred predominantly in the lung. Incidences of transitional cell papillomas and carcinomas in the urinary bladder were noted in male rats administered 2,000 ppm, together with an increased incidence of papillary and/or nodular hyperplasia of transitional epithelium. In mice, the incidence of papillary adenomas in the gall bladder, which is rare in mice, was increased in both males and females administered 2,000 ppm. Thus, o-PD is carcinogenic in two species, i.e., rats and mice of both sexes.     

The pharmacokinetics and macromolecular interactions of perchloroethylene in mice and rats as related to oncogenicity

The pharmacokinetic and macromolecular interactions of perchloroethylene were evaluated in B₆C₃F₁ mice and Sprague-Dawley rats in an attempt to explain, mechanistically, the sensitivity of the mouse and the resistance of the rat to perchloroethylene-induced hepatocellular carcinoma. When compared to rats, mice were found to metabolize 8.5 and 1.6 times more perchloroethylene per kilogram of body weight following inhalation of 10 ppm or a single oral dose of 500 mg/kg perchloro[¹⁴C]ethylene, respectively. Since the initial metabolism of perchloroethylene is an activation process, the increased extent of metabolism in the mouse resulted in a greater extent of irreversible binding of radioactivity in hepatic macromolecules of the mouse compared to that in the rat after inhalation of 10 or 600 ppm or a single oral dose of 500 mg/kg perchloro[¹⁴C]ethylene. Repeated oral administration of perchloroethylene for 11 days resulted in histopathological changes in the liver of mice at doses as low as 100 mg/kg/day, while minimal treatment-related effects were observed in the liver of rats only at the 1000 mg/kg/day level. Approximately a twofold increase in hepatic DNA synthesis, indicative of hepatic regeneration, was observed in mice but not in rats after repeated oral administration of perchloroethylene at dose levels which are tumorigenic to mice in lifetime studies. The absence of any pronouced direct interaction of perchloroethylene with hepatic DNA in mice at times of peak hepatic macromolecular binding suggests that hepatic tumors are induced in B₆C₃F₁ mice by recurrent cytotoxicity which enhances the spontaneous incidence of liver tumors in this highly susceptible strain of mouse. The implication of these results for hazard assessment is that recurrent tissue damage is necessary for tumors to be induced. Thus, levels of perchloroethylene which do not induce organ toxicity are not likely to pose a carcinogenic risk to man.     

Effect of Dichloroacetic Acid and Trichloroacetic Acid on DNA Methylation in Liver and Tumors of Female B6C3F1 Mice

Dichloroacetic acid (DCA) and trichloroacetic add (TCA) arefound in drinking water and are metabolites of trichloroethylene.They are carcinogenic and promote liver tumors in B6C3F1 mice.Hypomethylation of DNA is a proposed nongenotoxic mechanisminvolved in carcinogenesis and tumor promotion. We determinedthe effect of DCA and TCA on the level of DNA methylation inmouse liver and tumors. Female B6C3F1 mice 15 days of age wereadministered 25 mg/kg N-methyl-N-nitrosourea and at 6 weeksstarted to receive 25 mmol/liter of either DCA or TCA in theirdrinking water until euthanized 44 weeks later. Other animalsnot administered MNU were euthanized after 11 days of exposureto either DCA or TCA. DNA was isolated from liver and tumors,and after hydrolysis 5-methylcytosine (5MeC) and the four baseswere separated and quantitated by HPLC. In animals exposed toeither DCA or TCA for 11 days but not 44 weeks, the level of5MeC in DNA was decreased in the liver. 5MeC was also decreasedin liver tumors from animals exposed to either chloroaceticacid. The level of 5MeC in TCA-promoted carcinomas appearedto be less than in adenomas. Termination of exposure to DCA,but not to TCA, resulted in an increase in the level of 5MeCin adenomas to the level found in noninvolved liver. Thus, hypomethylatedDNA was found in DCA and TCA promoted liver tumors and the differencein the response of DNA methylation to termination of exposureappeared to support the hypothesis of different mechanisms fortheir carcinogenic activity.     

Inhalation Carcinogenicity and Chronic Toxicity of Carbon Tetrachloride in Rats and Mice

Carcinogenicity and chronic toxicity of carbon tetrachloride were examined by inhalation exposure of 50 F344 rats and 50 BDF1 mice of both sexes to carbon tetrachloride at 0 (clean air), 5, 25, or 125 ppm (v/v) for 6 h/day, 5 days/wk, for 104 wk. Incidences of hepatocellular adenomas and carcinomas in rats and mice of both sexes and of adrenal pheochromocytomas in mice of both sexes were significantly increased dose-dependently. Hepatocellular carcinomas and cirrhosis significantly occurred in the 125-ppm-exposed rats of both sexes, and 3 cases of hepatocellular carcinomas and increased incidences of hepatic altered cell foci were noted in the 25-ppm-exposed female rats. Hepatocellular carcinomas were induced in mice of both sexes at 25 and 125 ppm, and hepatocellular adenomas occurred in females at 5 ppm without any degenerative or necrotic change in hepatocytes. Hepatocellular carcinomas metastasized to the lung. The chronic hepatotoxicity was characterized by cirrhosis, fibrosis, and fatty change in rats, and ceroid deposition, bile-duct proliferation, and hydropic change in mice. Survival rates were decreased in the 125-ppm-exposed rats and mice of both sexes and in the 25-ppm-exposed female mice, in association with decreased body weights. The decreased survival rates were considered to be causally related to both various tumors including hepatocellular carcinomas and severe chronic progressive nephropathy in rats and to hepatocellular carcinomas in mice. This study provided clear evidence of carcinogenicity for carbon tetrachloride in rats and mice. A cytotoxic-proliferative and genotoxic mode of action for carbon tetrachloride-induced hepatocarcinogenesis was suggested.     

Carcinogenicity studies of 1,4-dioxane administered in drinking-water to rats and mice for 2 years

The carcinogenicity of 1,4-dioxane was examined by giving groups of 50 F344/DuCrj rats and 50 Crj:BDF₁ mice of each sex 1,4-dioxane in the drinking-water for 2 years. The concentrations of 1,4-dioxane were 0 (control), 200, 1000 and 5000 ppm (wt./wt.) for rats and 0, 500, 2000 and 8000 ppm for mice. The highest dose levels did not exceed the maximum tolerated dose. In the rat, there was significant induction of nasal squamous cell carcinomas in females and hepatocellular adenomas and carcinomas in males and females, peritoneal mesotheliomas in males, and mammary gland adenomas in females. In the mouse, there was significant induction of hepatocellular tumors in males and females. Two nasal tumors occurring in the 8000 ppm-dosed groups were spontaneously rare and, thus, were attributed to 1,4-dioxane exposure. The present studies provided clear evidence of carcinogenicity in rats and mice. Lifetime cancer risk of humans exposed to 1,4-dioxane through drinking-water was quantitatively estimated with a non-threshold approach by application of a linearized multistage model to dose–carcinogenic response relationships, in addition to a threshold approach for estimation of the tolerable daily intake using no-observed- or lowest-observed-adverse-effect levels of the carcinogenic responses and uncertainty factors.     

Inhalation carcinogenicity and chronic toxicity of carbon tetrachloride in rats and mice

Carcinogenicity and chronic toxicity of carbon tetrachloride were examined by inhalation exposure of 50 F344 rats and 50 BDF1 mice of both sexes to carbon tetrachloride at 0 (clean air), 5, 25, or 125 ppm (v/v) for 6 h/day, 5 days/wk, for 104 wk. Incidences of hepatocellular adenomas and carcinomas in rats and mice of both sexes and of adrenal pheochromocytomas in mice of both sexes were significantly increased dose-dependently. Hepatocellular carcinomas and cirrhosis significantly occurred in the 125-ppm-exposed rats of both sexes, and 3 cases of hepatocellular carcinomas and increased incidences of hepatic altered cell foci were noted in the 25-ppm-exposed female rats. Hepatocellular carcinomas were induced in mice of both sexes at 25 and 125 ppm, and hepatocellular adenomas occurred in females at 5 ppm without any degenerative or necrotic change in hepatocytes. Hepatocellular carcinomas metastasized to the lung. The chronic hepatotoxicity was characterized by cirrhosis, fibrosis, and fatty change in rats, and ceroid deposition, bile-duct proliferation, and hydropic change in mice. Survival rates were decreased in the 125-ppm-exposed rats and mice of both sexes and in the 25-ppm-exposed female mice, in association with decreased body weights. The decreased survival rates were considered to be causally related to both various tumors including hepatocellular carcinomas and severe chronic progressive nephropathy in rats and to hepatocellular carcinomas in mice. This study provided clear evidence of carcinogenicity for carbon tetrachloride in rats and mice. A cytotoxic-proliferative and genotoxic mode of action for carbon tetrachloride-induced hepatocarcinogenesis was suggested.     

Correlation between Bcl-2 overexpression and H-ras mutation in naturally occurring hepatocellular proliferative lesions of the B6C3F1 mouse.

The correlation between the mutation at codon 61 of the H-ras gene and the expression of the Bcl-2 protein was investigated in naturally occurring hepatocellular proliferative lesions in B6C3F1 mice. Specimens of histologically diagnosed neoplastic or preneoplastic lesions of the liver, obtained from the control mice used for 2-year carcinogenicity studies, were examined by immunohistochemical techniques. All of 25 lesions confirmed to be hepatocellular carcinomas stained positive for the Bcl-2 protein. Three of 12 foci of cellular alterations, as well as 24 of 42 hepatocellular adenomas, stained weakly positive. Bcl-2 protein was expressed to a greater degree in hepatocellular carcinomas as opposed to adenomas and confirmed by Western blot analysis. Seven of 18 hepatocellular adenomas that stained positive for Bcl-2 and three of 16 hepatocellular adenomas that stained negative had a mutation at codon 61 of the H-ras gene. Overexpression of Bcl-2 protein is likely to enhance the malignant turnover of the neoplastic cells, following a mutation at codon 61 of the H-ras gene particularly. These findings suggest that Bcl-2 overexpression and the mutation at codon 61 of the H-ras gene may be critical factors in the development of naturally occurring hepatocellular tumors in B6C3F1 mice.     

Trichloroacetic acid: updated estimates of its bioavailability and its contribution to trichloroethylene-induced mouse hepatomegaly

Trichloroacetic acid (TCA) is a common drinking water disinfection byproduct that produces a spectrum of liver effects, including hepatomegaly and liver tumors, in mice. It is also an oxidative metabolite of trichloroethylene (TCE), a solvent used in degreasing with widespread environmental exposure, which also produces hepatomegaly and liver tumors in mice. Physiologically based pharmacokinetic (PBPK) modeling of TCE and TCA can be used to quantitatively compare the dose-responses for hepatomegaly for these two chemicals on the basis of internal TCA dose, and thereby test the hypothesis that TCA could fully explain TCE-induced hepatomegaly. Previously, using a PBPK model calibrated using kinetic data from i.v. and gavage dosing of TCA and from TCA produced from TCE, it was concluded that TCA accounted for only about one-fifth of the degree of hepatomegaly produced by TCE. However, recently available data suggest a non-linear change in internal TCA dose attributed to a dose-dependent fractional absorption of TCA administered in drinking water, the primary route of exposure of TCA both environmentally and in experimental toxicity studies. Therefore, in the present reanalysis, the PBPK modeling of TCA was updated using these data and the comparison between TCA- and TCE-induced hepatomegaly was revisited using updated internal dose predictions. With respect to updated PBPK modeling results, incorporating less than complete absorption of TCA administered in drinking water substantially improves the PBPK model fit to the newly available data, based on goodness-of-fit comparison. However, inter-experimental variability is high, with nearly complete absorption estimated for some studies. With respect to the comparison of TCA and TCA-induced hepatomegaly, this reanalysis predicts that TCA can account for roughly one-third to one-half of the effect observed with TCE - greater than previously reported, but still inconsistent with TCA being the sole active moiety for this effect. However, given uncertainty as to the precise degree of contribution of TCA and due to high inter-experimental variability in estimated fractional absorption, a more precise quantitative estimate of the relative contribution of TCA may obtained through an appropriate experiment in mice simultaneously measuring TCA kinetics and TCE- and TCA-induced hepatomegaly.     

Importance of the mouse liver tumor in carcinogenesis bioassay studies using benzidine dihydrochloride as a model

Benzidine dihydrochloride induced hepatocellular adenomas in male and female mice which appeared to progress to hepatocellular carcinomas as either the length of administration and/or the dose level of benzidine increased. The differentiation of hepatocellular carcinomas also correlated inversely with dose, and poorly differentiated hepatocellular carcinomas metastasized more frequently. These findings support the view that the mouse liver tumor is predictive of carcinogenicity in bioassay studies.     

Hepatocarcinogenicity of Chioral Hydrate, 2-Chloroacetaldehyde, and Dichioroacetic Acid in the Male B6C3F1 Mouse

The chlorinated acetaldehydes, chloral hydrate (CH) and 2-chloroacetaldehyde(CAA), have been identified as chlorination by-products in finisheddrinking water supplies. Although both chemicals are genotoxic,their potential for carcinogenicity had not been adequatelyexplored. The studies reported here are chronic bioassays conductedwith male B6C3F1 mice exposed to levels of 1 g/liter CH and0.1 g/liter CAA via the drinking water for 104 weeks. Distilledwater (H₂O) served as the untreated control and dichloroaceticacid (DCA; 0.5 g/liter), another chlorine disinfection by-product,was included. The mean daily ingested doses were approximately166 mg/kg/day for CH, 17 mg/kg/day for CAA, and 93 mg/kg/dayfor DCA. Evaluations included mortality, body weight, organweights, gross pathology, and histopathology. The primary targetorgan was the liver as the organ weights and pathological changesin the other organs (spleen, kidneys, and testes) were comparablebetween the treated groups and the H₂O control group. Liverweights were increased for all three test chemicals at the terminaleuthanasia with the greatest increase seen in the CH and DCAgroups. Hepatocellular necrosis was induced by all three testchemicals, and it was also most prevalent and severe in theCH and DCA groups. A significant increase in the prevalenceof liver tumors was seen for all three chemicals. The strongestresponse was with DCA, in which 63% of the 104-week survivorshad hepatocellular carcinomas (carcinomas) and 42% possessedhepatocellular adenomas (adenomas) and the combined prevalencefor carcinomas plus adenoma was 75%. The corresponding prevalencerate for carcinomas, adenomas, and combined tumors were 46,29, and 71% 31, 8, and 38% and 10, 5, and 15% for CH, CAA, andH₂O, respectively. In addition to the tumors we evaluated theprevalence of a possible preneoplastic lesion, the hepatocellularhyperplastic nodule (nodules), a lesion which occurred in allthree treated groups but not in the H₂O group.     

Application of the margin of exposure (MOE) approach to substances in food that are genotoxic and carcinogenic. Example: Leucomalachite green

Leucomalachite green (LMG) is mutagenic and produces DNA-adducts in vivo, and is carcinogenic in rodent bioassays. Dose-response modelling of the data for hepatocellular adenomas and carcinomas in female mice gave a BMDL10 of 20 mg/kg-bw/day. Limited data are available on the concentrations present in fish for human consumption. Human exposure estimates assumed that all consumed fish is contaminated with LMG. The calculated MoEs were 4,000,000 and 400,000 respectively for average and high exposure estimates.